JP2818253B2 - Dissolution method of iron-based scrap contaminated with radioactive materials - Google Patents
Dissolution method of iron-based scrap contaminated with radioactive materialsInfo
- Publication number
- JP2818253B2 JP2818253B2 JP9506190A JP9506190A JP2818253B2 JP 2818253 B2 JP2818253 B2 JP 2818253B2 JP 9506190 A JP9506190 A JP 9506190A JP 9506190 A JP9506190 A JP 9506190A JP 2818253 B2 JP2818253 B2 JP 2818253B2
- Authority
- JP
- Japan
- Prior art keywords
- slag
- iron
- less
- radioactive materials
- based scrap
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
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- Processing Of Solid Wastes (AREA)
- Gasification And Melting Of Waste (AREA)
- Carbon Steel Or Casting Steel Manufacturing (AREA)
Description
【発明の詳細な説明】 [産業上の利用分野] 本発明は解体された原子力発電設備等、放射性物質で
汚染された鉄系スクラップを、放射性物質が系外に拡散
することなく安全に溶解する方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION [Industrial Application Field] The present invention safely dissolves iron-based scrap contaminated with radioactive materials, such as dismantled nuclear power plants, without the radioactive materials diffusing out of the system. It is about the method.
[従来の技術] 放射性物質で汚染された鉄系スクラップを溶解するた
めに、従来は集塵設備を備えるか、密閉構造を有する誘
導炉、アーク炉などで溶解し、精錬を行っている。しか
し、放射性物質をスラグ、メタル以外に拡散させないた
めの溶解条件については知られていないし、例えば、下
記の報告にも記載はない。D.S.Harvey:Melting of co
ntaminates steel scrap from decommissioning(Proce
eding of 1989 International Conference on the Deco
mmissioning of Nuclear Installations.24−27 Oct.,1
989,Brussels p.422−430)、M.Sappok and G.Lukac
s:Melting of Radioactive Metal Scrap from Nuclear
Installations(ibid.,p431−442)。[Prior Art] In order to dissolve iron-based scrap contaminated with radioactive materials, conventionally, dusting equipment is provided, or melting and refining is performed in an induction furnace or arc furnace having a closed structure. However, there is no known dissolution condition for preventing the radioactive substance from diffusing other than slag and metal, and for example, there is no description in the following report. DSHarvey: Melting of co
ntaminates steel scrap from decommissioning (Proce
eding of 1989 International Conference on the Deco
mmissioning of Nuclear Installations. 24-27 Oct., 1
989, Brussels p.422-430), M. Sappok and G. Lukac
s: Melting of Radioactive Metal Scrap from Nuclear
Installations (ibid., P431-442).
[発明が解決しようとする課題] 従来の方法では、原料の鉄系スクラップに含まれる放
射性物質、特にセシウム及びマンガンがヒュームやダス
トとなって飛散する場合が多い。このため、集塵等の排
ガス処理設備並びにその操業が大規模かつ複雑になる。
というのは、溶鉄及びスラグの温度が一時的かつ局所的
にせよ高温になり、かつスラグ組成に対する検討が十分
に行われていないために生じる問題である。本発明の目
的は、かかる問題を解決することにあり、放射性物質を
スラグまたは溶鉄に集中させて、ヒューム、ダストに移
行する割合を著減させることのできる放射性物質で汚染
された鉄系スクラップの溶解方法を提供するものであ
る。[Problems to be Solved by the Invention] In the conventional method, radioactive substances, particularly cesium and manganese, contained in the raw iron-based scrap are often scattered as fumes and dust. For this reason, exhaust gas treatment equipment such as dust collection and its operation become large-scale and complicated.
This is a problem that occurs because the temperature of molten iron and slag becomes high, even temporarily and locally, and the slag composition is not sufficiently studied. An object of the present invention is to solve such a problem, and concentrates radioactive materials on slag or molten iron, thereby reducing the rate of transfer to fumes and dust. It provides a dissolution method.
[課題を解決するための手段] 本発明の要旨とするところは、(1)放射性物質で汚
染された鉄系スクラップを溶解するに当たり、鉄浴温度
を1400℃以下、溶解する鉄の炭素含有量を3%以上と
し、かつスラグ組成をスラグ中において酸化珪素に対す
る酸化カルシウムの重量比として0.3以上、1.0以下とす
ることを特徴とする放射性物質で汚染された鉄系スクラ
ップの溶解方法であり、また(2)スラグ中への弗化物
の添加量が弗素分としてスラグの塩基度が0.5超1.0以下
のときは1.5%以上、18%未満、スラグの塩基度が0.5以
下のときは1.5%以上、12%未満であることを特徴とす
る前記(1)に記載の放射性物質で汚染された鉄系スク
ラップの溶解方法である。[Means for Solving the Problems] The gist of the present invention is to (1) dissolve iron-based scrap contaminated with radioactive materials, set the iron bath temperature to 1400 ° C or less, and dissolve the carbon content of iron. Is 3% or more, and the slag composition is 0.3 to 1.0 in weight ratio of calcium oxide to silicon oxide in the slag, and is a method for dissolving iron-based scrap contaminated with radioactive materials. (2) The amount of fluoride added to the slag is 1.5% or more and less than 18% when the basicity of the slag is more than 0.5 and 1.0 or less as fluorine, and 1.5% or more when the basicity of the slag is 0.5 or less. The method for dissolving an iron-based scrap contaminated with a radioactive substance according to the above (1), which is less than 12%.
以下に本発明の詳細を作用と共に説明する。 The details of the present invention will be described below together with the operation.
[作用] 本発明における原料の鉄系スクラップは、主として鋼
スクラップであるが、使用済み原子力発電設備等を解体
して得たスクラップであり、この中には圧力容器、各種
配管、機器類、建屋、基礎等の構造物が含まれる。従っ
て、原子炉使用に伴い生成する、放射性のコバルト、マ
ンガン、セシウム、ストロンチウム等がスクラップを汚
染する放射性物質として含まれている。スクラップは放
射能レベルにより、分類、仕分しておき、更に除染等に
より、放射能レベルを低減しておくことが好ましい。[Operation] The iron-based scrap as the raw material in the present invention is mainly steel scrap, but scrap obtained by dismantling used nuclear power generation equipment and the like, and includes pressure vessels, various pipes, equipment, buildings, and the like. , Foundations and other structures. Therefore, radioactive cobalt, manganese, cesium, strontium, and the like generated with the use of a nuclear reactor are included as radioactive substances contaminating scrap. It is preferable that the scrap is classified and sorted according to the radioactivity level, and the radioactivity level is further reduced by decontamination or the like.
スクラップは全量を最初から装入してもよいし、あら
かじめ種湯を溶解しておいてこれに添加する方式で装入
してもよい。The scrap may be charged in its entirety from the beginning, or may be charged by dissolving the seed water in advance and adding it.
本発明に用いられる溶解炉は放射性物質の拡散を防止
するため、密閉可能な構造となっており、スクラップ、
コークス及び媒溶剤等の副原料の装入口、溶鉄及びスラ
グの排出口と排ガスの吸引及び集塵機構を備えている。
操業の制御が容易であるという点で、アーク溶解炉、プ
ラズマ溶解炉、誘導溶解炉等の電気溶解炉が好ましい。
ダストの中に含まれる放射性物質が全量集塵系を通り、
系外に逸出しないようにするため、稼動中は溶解炉内の
圧力を大気圧より低く保つ。The melting furnace used in the present invention has a sealable structure to prevent the diffusion of radioactive materials, scrap,
It is equipped with an inlet for auxiliary materials such as coke and a solvent, an outlet for molten iron and slag, and an exhaust gas suction and dust collection mechanism.
An electric melting furnace such as an arc melting furnace, a plasma melting furnace, or an induction melting furnace is preferable in that the operation is easily controlled.
All radioactive substances contained in the dust pass through the dust collection system,
During operation, the pressure inside the melting furnace is kept lower than the atmospheric pressure so as not to escape from the system.
放射性物質、特にセシウムがヒュームとなってダスト
に逸散することを抑制し、かつスラグ中に留まるたの条
件を種々調査検討した結果、溶鉄を高炭素組成として溶
解時の温度を低く保つこと、及び、スラグの塩基度を低
く保つことが必須であることがわかった。即ち、具体的
にはセシウムの80%以上をスラグ中に留めるために、14
00℃以下とすることが必要であり、できれば1350℃以下
とするのが好ましい。誘導溶解炉では溶鉄の温度よりも
スラグの温度の方が低くなるので、セシウムをスラグ中
に留める上で一層有利である。アーク溶解炉ではスラグ
の温度が溶鉄の温度よりも高くなるので、より低温で操
業することが好ましい。As a result of investigating the conditions for radioactive substances, especially cesium to become fumes and escaping into dust, and remaining in the slag, the molten iron has a high carbon composition and the temperature at the time of melting is kept low. And it was found that it was essential to keep the basicity of the slag low. That is, in order to keep more than 80% of cesium in slag,
It is necessary to keep the temperature at 00 ° C. or lower, and preferably at 1350 ° C. or lower if possible. Since the temperature of the slag is lower than the temperature of the molten iron in the induction melting furnace, it is more advantageous in retaining cesium in the slag. Since the temperature of the slag is higher than the temperature of the molten iron in the arc melting furnace, it is preferable to operate at a lower temperature.
低温で操業するためには溶鉄が高炭素組成であること
が必要である。溶解中の安定操業、及び、出湯鋳造時の
流動性を保持するために溶鉄中の炭素濃度は3%以上が
必要であり、さらに高い方が有利である。より低温操業
を可能にするためには炭素濃度4%以上が好ましい。溶
鉄が高炭素組成であることはスラグの酸化の程度を低く
保つのに有利であり、これはセシウムやマンガンがダス
トへ移行するのを抑制する効果がある。In order to operate at a low temperature, the molten iron needs to have a high carbon composition. In order to maintain stable operation during melting and maintain fluidity at the time of tapping, the concentration of carbon in the molten iron must be 3% or more, and a higher concentration is more advantageous. In order to enable a lower temperature operation, the carbon concentration is preferably 4% or more. The fact that the molten iron has a high carbon composition is advantageous for keeping the degree of slag oxidation low, which has the effect of suppressing the transfer of cesium and manganese to dust.
スラグの塩基度は、一般にスラグ中において酸化珪素
に対する酸化カルシウムの重量比で定義する。放射性物
質、特に、セシウムがスラグ中に留まり、ヒュームとな
ってダストに逸散することを抑制するために、塩基度は
1.0以下とすることが必要である。さらに、スラグが溶
融状態にある限り、この塩基度が低い程逸散抑制には有
利であることから、できれば0.6以下がより好ましい。
しかし塩基度があまり低くなり過ぎるとスラグの融点が
上昇し、1400℃以下の鉄浴温度で溶融スラグとならない
ため0.3以上が必要である。スクラップ溶解が進行する
に従ってスラグ中に酸化珪素が蓄積するので、溶解の全
期間を通して塩基度を所定の範囲に保つことが重要であ
る。スラグの塩基度が低いと凝固冷却したスラグはガラ
ス状となり、物理的にも化学的にも安定であるという利
点がある。また、誘導溶解炉を使用する場合、スラグの
塩基度が低いことは炉体耐火物の損耗抑制のためにも有
利である。The basicity of slag is generally defined by the weight ratio of calcium oxide to silicon oxide in the slag. In order to prevent radioactive substances, especially cesium from remaining in the slag and fumes and escaping into dust,
It must be less than 1.0. Further, as long as the slag is in a molten state, the lower the basicity, the more advantageous the suppression of escape.
However, if the basicity is too low, the melting point of the slag increases, and the slag does not become a molten slag at an iron bath temperature of 1400 ° C. or less. Since silicon oxide accumulates in the slag as the scrap melting progresses, it is important to keep the basicity within a predetermined range throughout the melting. If the basicity of the slag is low, the slag solidified and cooled becomes glassy, and has the advantage of being physically and chemically stable. When an induction melting furnace is used, the low basicity of the slag is also advantageous for suppressing the wear of the furnace refractory.
本発明はスラグ中に適量の弗化物を添加することによ
り、低温操業においても良好なスラグ流動性を確保しつ
つ炉体耐火物の損耗抑制をはかることに成功した。In the present invention, by adding an appropriate amount of fluoride to the slag, it has succeeded in suppressing the wear of the furnace refractory while maintaining good slag fluidity even in low-temperature operation.
弗化物は酸化物スラグの融点を引き下げ、低温での流
動性を増加させる効果があり、その量が多いほど効果も
大きいことは知られている。しかし本発明のような低塩
基度のスラグ中で弗素分が多くなるとダスト量が多くな
り、塩基度も時間と共に増加する欠点のあることが分か
った。同時に排ガス中の弗素分も増加し、耐火物が侵食
されやすくなる。従って、弗化物の添加が多過ぎるのは
好ましくない。Fluoride has the effect of lowering the melting point of oxide slag and increasing the fluidity at low temperatures, and it is known that the greater the amount, the greater the effect. However, it has been found that when the fluorine content increases in a low basicity slag as in the present invention, the amount of dust increases and the basicity also increases with time. At the same time, the fluorine content in the exhaust gas also increases, and the refractories are easily eroded. Therefore, it is not preferable to add too much fluoride.
本発明者らはスラグ中に添加する弗化物の種類及び量
を種々検討した結果、最適弗化物の種類と最適添加量を
見い出した。即ち、添加弗化物の種類としては熱的、化
学的安定性から弗化カルシウム、弗化ナトリウムが適当
であり、特に純度を上げた天然の蛍石が最適である。As a result of various studies on the type and amount of fluoride added to the slag, the present inventors have found out the type and optimum amount of fluoride to be added. That is, calcium fluoride and sodium fluoride are suitable as the kind of the added fluoride from the viewpoint of thermal and chemical stability, and natural fluorite having a higher purity is most suitable.
添加量は弗素分として1.5%以上が有効であり、4%
以上で効果が顕著になる。添加量が増すとダスト量も多
くなり、スラグの塩基度が0.5超1.0以下のときは18%以
上、スラグの塩基度が0.5以下のときは12%以上で操業
や排ガスの後処理が困難になる。従って、弗化物の添加
量は弗素分として塩基度が0.5超1.0以下のときは1.5%
以上、18%未満が、また塩基度が0.5以下のときは1.5%
以上、12%未満が有用範囲である。It is effective to add 1.5% or more of fluorine, and 4%
As described above, the effect becomes remarkable. As the amount of addition increases, the amount of dust also increases. When the basicity of the slag is more than 0.5 and less than 1.0, it is 18% or more, and when the basicity of the slag is less than 0.5, it is more than 12%. Become. Therefore, the amount of fluoride added is 1.5% when the basicity is more than 0.5 and 1.0 or less in terms of fluorine.
Above, less than 18%, and 1.5% when the basicity is 0.5 or less
As mentioned above, the useful range is less than 12%.
[実施例] 密閉構造を有し、排ガスの吸引処理設備を備え、シリ
カ質不定型炭化物でライニングした0.5トンの低周波誘
導溶解炉に、解体した原子炉構造物で低レベル放射能の
スクラップ350kgを16kgのコークスと共に装入し、炉内
を大気圧に対して減圧した状態に維持しながら溶解し
た。フラックスとして生石灰1kgと蛍石0.1kgを溶け落ち
前に添加した。温度1250〜1330℃で溶解、精錬し、1310
℃で炉底からスラグと共に出湯し、鋳型に鋳造した。得
られた鉄の成分はC 3.8%,Si 0.62%,Mn 0.35%,スラ
グはCaO 17.8%,SiO2 55.2%,T.Fe 2.5%,CaF2 3.3%,C
s 0.05%であった。電気集塵機及びシックナーから回収
したダスト量は0.5kgで極めて少なかった。ダストの成
分はSiO2 13.4%,CaO 3.3%,残分は鉄でCsは検出され
なかった。[Example] In a 0.5 ton low-frequency induction melting furnace equipped with a closed structure, equipped with exhaust gas suction treatment equipment, and lined with siliceous amorphous carbide, dismantled reactor structure and 350 kg of low-level radioactive scrap Was charged together with 16 kg of coke and melted while maintaining the inside of the furnace at a reduced pressure with respect to the atmospheric pressure. As a flux, 1 kg of quicklime and 0.1 kg of fluorite were added before meltdown. Melted and refined at a temperature of 1250-1330 ° C, 1310
At ℃, the molten metal was discharged from the furnace bottom together with the slag and cast into a mold. The obtained iron component is C 3.8%, Si 0.62%, Mn 0.35%, slag is CaO 17.8%, SiO 2 55.2%, T.Fe 2.5%, CaF 2 3.3%, C
s 0.05%. The amount of dust collected from the electric dust collector and the thickener was very small at 0.5 kg. The dust component was SiO 2 13.4%, CaO 3.3%, and the balance was iron with no Cs detected.
凝固したスラグはガラス質であり、その放射能は0.00
013μCi/g、ダストの放射能は0.00001μCi/g以下であっ
た。The solidified slag is vitreous, its radioactivity is 0.00
013 μCi / g and the radioactivity of dust was 0.00001 μCi / g or less.
比較例として、同じ原料スクラップを5kgのコークス
と共に溶解した。フラックスは生石灰6kgを溶け落ち前
に添加した。温度1450〜1565℃で溶解し、溶解後直ち
に、1540℃で炉底からスラグと共に出湯し、鋳型に鋳造
した。得られた鉄の成分はC 0.5%,Si 0.30%,Mn 0.28
%,スラグはCaO 36.8%,SiO2 31.5%,T.Fe 4.5%,Cs
0.01%以下であった。電気集塵機及びシックナーから回
収したダスト量は3.5kgであった。ダストの成分はSiO2
9.6%,CaO 11.2%残分は主に鉄でCs 0.03%であった。As a comparative example, the same raw material scrap was melted together with 5 kg of coke. The flux added 6 kg of quicklime before burnt off. Melting was carried out at a temperature of 1450 to 1565 ° C, and immediately after melting, tapping was carried out together with slag from the furnace bottom at 1540 ° C and cast into a mold. The obtained iron components are C 0.5%, Si 0.30%, Mn 0.28
%, Slag is CaO 36.8%, SiO 2 31.5%, T.Fe 4.5%, Cs
It was less than 0.01%. The amount of dust collected from the electric dust collector and the thickener was 3.5 kg. The component of dust is SiO 2
The 9.6%, CaO 11.2% residue was mainly iron and Cs 0.03%.
凝固したスラグは結晶質であり、スラグの放射能は0.
00009μCi/gであった。ダストの放射能は0.00014μCi/g
と前述の本発明実施例より10倍以上の値となり、はるか
に高かった。The solidified slag is crystalline, and the radioactivity of the slag is 0.
00009 μCi / g. The radioactivity of dust is 0.00014μCi / g
And 10 times or more the value of the above-mentioned embodiment of the present invention, which is much higher.
[発明の効果] 本発明により、放射性物質で汚染された鉄系スクラッ
プをダスト、排ガス、排水処理など環境対策に過大な負
担を掛けることなく溶解でき、放射性物質を鉄と安定な
ガラス状スラグに移行できる。これにより、解体原子炉
からの鉄系スクラップを小体積で拡散の危険がない状態
にして保管できる利点がある。また鉄の放射能レベルが
低い場合には鋳鉄や鋼材原料として再利用を図ることも
可能である。[Effect of the Invention] According to the present invention, iron-based scrap contaminated with radioactive material can be dissolved without imposing an excessive burden on environmental measures such as dust, exhaust gas, and wastewater treatment, and the radioactive material is converted into iron and stable glassy slag. Can be migrated. Thereby, there is an advantage that iron-based scrap from a dismantled nuclear reactor can be stored in a small volume with no danger of diffusion. When the radioactivity level of iron is low, it can be reused as a raw material for cast iron or steel.
Claims (2)
溶解するに当たり、鉄浴温度を1400℃以下、溶解する鉄
の炭素含有量を3%以上とし、かつスラグ組成をスラグ
中において酸化珪素に対する酸化カルシウムの重量比と
して0.3以上、1.0以下とすることを特徴とする放射性物
質で汚染された鉄系スクラップの溶解方法。(1) In dissolving iron-based scrap contaminated with radioactive materials, the iron bath temperature is set to 1400 ° C. or less, the carbon content of the dissolved iron is set to 3% or more, and the slag composition is reduced to silicon oxide in the slag. A method for dissolving iron-based scrap contaminated with radioactive materials, wherein the weight ratio of calcium oxide is 0.3 or more and 1.0 or less.
てスラグ中において酸化珪素に対する酸化カルシウムが
重量比で0.5超1.0以下のときは1.5%以上、18%未満、
また0.5以下のときは1.5%以上、12%未満であることを
特徴とする請求項(1)に記載の放射性物質で汚染され
た鉄系スクラップの溶解方法。2. When the weight ratio of calcium oxide to silicon oxide in the slag is more than 0.5 and 1.0 or less in the slag, the amount of fluoride added to the slag is 1.5% or more and less than 18%.
The method for dissolving iron-based scrap contaminated with radioactive materials according to claim 1, wherein when the ratio is 0.5 or less, the ratio is 1.5% or more and less than 12%.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9506190A JP2818253B2 (en) | 1990-04-12 | 1990-04-12 | Dissolution method of iron-based scrap contaminated with radioactive materials |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9506190A JP2818253B2 (en) | 1990-04-12 | 1990-04-12 | Dissolution method of iron-based scrap contaminated with radioactive materials |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH03293599A JPH03293599A (en) | 1991-12-25 |
| JP2818253B2 true JP2818253B2 (en) | 1998-10-30 |
Family
ID=14127512
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP9506190A Expired - Lifetime JP2818253B2 (en) | 1990-04-12 | 1990-04-12 | Dissolution method of iron-based scrap contaminated with radioactive materials |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2818253B2 (en) |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| FR2732475B1 (en) * | 1995-04-03 | 1997-04-30 | Commissariat Energie Atomique | METHOD AND DEVICE FOR CONTINUOUS MONITORING OF DUST ACTIVITY |
| JP6524532B2 (en) * | 2015-12-25 | 2019-06-05 | 清水建設株式会社 | Purification method of iron containing radioactive cesium |
| JP7143030B2 (en) * | 2018-10-05 | 2022-09-28 | Jfeエンジニアリング株式会社 | Manufacturing method of clearance metal |
| JP7143029B2 (en) * | 2018-10-05 | 2022-09-28 | Jfeエンジニアリング株式会社 | Manufacturing method of clearance metal |
-
1990
- 1990-04-12 JP JP9506190A patent/JP2818253B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPH03293599A (en) | 1991-12-25 |
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